Suckler cow and calf on a re-wetted fen (Norbert Röder (Thünen-Institute of Rural Studies, Bundesallee 50, D-38116, Braunschweig, Germany))
In peat lands, formed over centuries, reducing the ground water level leads to min-eralization: this results in greenhouse gas (GHG) emissions and leaching of dis-solved organic nutrients into adjacent water bodies. Furthermore, drainage leads to the destruction of highly specialized ecosystems. Re-wetting, by removing of drain-age systems (etc.), means the restoration of a higher ground water level which can reduce GHG emissions in the long term. Re-wetting to a water-level of 10 cm below the soil surface is ideal for reducing GHG emissions and preventing peat mineraliza-tion. One prerequisite for re-wetting is that soil degradation and peat mineralization are not too advanced. An adequate water supply must be available. Re-wetting also affects adjacent areas so possible impacts such as flooding of settlements and in-frastructure must be considered.
Purpose of the Technology: Land uses suitable for the soil conditions after re-wetting are extensive grazing, or paludiculture. Paludiculture is the cultivation of wet organic soils by preserving or renewing peat by planting and harvesting specific trees (e.g. alder), reeds and sedges. On fens, alder trees (for wood /biomass production) or plant species grown for their products (e.g. for thatch) or bioenergy, including the common reed, reed canary grass or cat’s-tail, can be cultivated. On peat bogs sphagnum farming as a peat substitute in horticulture, or as a medicinal plant, is possible. The first harvest of the common reed can take place four years post-establishment; thereafter annually. Alternatively, extensive livestock grazing with water buffalo or suitable breeds of cattle like Galloway or Heck has potential for re-wetted land. Year-round grazing is possible with a carrying capacity of up to 0.7 livestock units/ha.
Establishment / maintenance activities and inputs: Apart from avoiding huge amounts of GHG emissions and bringing land into alter-native production, further aims of re-wetting and adapting land use are:
-soil protection (soil structure, water content, peat protection);
-water protection (water quality, buffering / filtering water);
-protection of the landscape’s water regime and material balance (solute transport);
-biodiversity protection (retaining a sensitive ecosystem with specialized/ threatened species); and
-flood protection (organic soils can quickly absorb large amount of water).
There are many advantages for the environment while still creating a (modest) in-come for land users. Unlike most other bioenergy production chains (e.g. maize, rapeseed) which do not have these environmental co-benefits, paludiculture with the common reed can become a sustainable production system.
Natural / human environment: The Altmark region is located on the North German Plain. The region is predomi-nantly characterized by agriculture but has many forests too. Because of the high proportion of grassland, cattle are important. The use of biomass for bioenergy was increasing and many biogas plants were established in the last few years. Fens are mostly located in Altmark-County Salzwedel. Here, the average population density (42.7 inhabitants km2) is relatively low in the German context and the annual precipi-tation of 466mm is also below the overall German average.
ສະຖານທີ່: Altmarkkreis Salzwedel and district Stendal (total area of region: 4744 km²), Germany, Saxony-Anhalt, ເຢຍລະມັນ
ຈໍານວນ ພື້ນທີ່ ທີ່ໃຊ້ ເຕັກໂນໂລຢີ ທີ່ໄດ້ວິເຄາະ:
ການແຜ່ກະຈາຍຂອງເຕັກໂນໂລຢີ:
ຢູ່ໃນເຂດປ່າສະຫງວນທີ່ບໍ?:
ວັນທີຂອງການປະຕິບັດ: ຕໍ່າກວ່າ 10 ປີ ຜ່ານມາ (ມາເຖິງປະຈຸບັນ)
ປະເພດຂອງການນໍາສະເໜີ
| ລະບຸ ປັດໃຈ ນໍາເຂົ້າ ໃນການຜະລີດ | ຫົວໜ່ວຍ | ປະລິມານ | ຕົ້ນທຶນ ຕໍ່ຫົວໜ່ວຍ (n.a.) | ຕົ້ນທຶນທັງໝົດ ຂອງປັດໃຈຂາເຂົ້າ ໃນການຜະລິດ (n.a.) | % ຂອງຕົ້ນທຶນທັງໝົດ ທີ່ຜູ້ນໍາໃຊ້ທີ່ດິນ ໃຊ້ຈ່າຍເອງ |
| ແຮງງານ | |||||
| Labour | ha | 1.0 | 300.0 | 300.0 | 100.0 |
| ອຸປະກອນ | |||||
| Machine use | ha | 1.0 | 400.0 | 400.0 | 100.0 |
| ວັດສະດຸໃນການປູກ | |||||
| Seedling | ha | 1.0 | 2500.0 | 2500.0 | 100.0 |
| ອື່ນໆ | |||||
| Removal of drainage | ha | 1.0 | 200.0 | 200.0 | 100.0 |
| Ditch filling | ha | 1.0 | 100.0 | 100.0 | 100.0 |
| Make-ready and set-up cost | ha | 1.0 | 2500.0 | 2500.0 | 100.0 |
| ຕົ້ນທຶນທັງໝົດ ໃນການຈັດຕັ້ງປະຕິບັດ ເຕັກໂນໂລຢີ | 6'000.0 | ||||
| ຄ່າໃຊ້ຈ່າຍທັງໝົດ ສຳລັບການສ້າງຕັ້ງເຕັກໂນໂລຢີ ເປັນສະກຸນເງີນໂດລາ | 6'000.0 | ||||
| ລະບຸ ປັດໃຈ ນໍາເຂົ້າ ໃນການຜະລີດ | ຫົວໜ່ວຍ | ປະລິມານ | ຕົ້ນທຶນ ຕໍ່ຫົວໜ່ວຍ (n.a.) | ຕົ້ນທຶນທັງໝົດ ຂອງປັດໃຈຂາເຂົ້າ ໃນການຜະລິດ (n.a.) | % ຂອງຕົ້ນທຶນທັງໝົດ ທີ່ຜູ້ນໍາໃຊ້ທີ່ດິນ ໃຊ້ຈ່າຍເອງ |
| ແຮງງານ | |||||
| Labour | ha | 1.0 | 250.0 | 250.0 | 100.0 |
| ອຸປະກອນ | |||||
| Machine use | ha | 1.0 | 600.0 | 600.0 | 100.0 |
| ອື່ນໆ | |||||
| Management | ha | 1.0 | 150.0 | 150.0 | 100.0 |
| ຕົ້ນທຶນທັງໝົດ ທີ່ໃຊ້ໃນການບໍາລຸງຮັກສາ ເຕັກໂນໂລຢີ | 1'000.0 | ||||
| ຄ່າໃຊ້ຈ່າຍທັງໝົດ ສຳລັບການບົວລະບັດຮກສາເຕັກໂນໂລຢີ ເປັນສະກຸນເງີນໂດລາ | 1'000.0 | ||||
Thorugh extensification
possibly
Thorugh extensification
In terms of former cropland
Extensive usage
ປະລິມານ ກ່ອນການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ: 15-30
ປະລີມານ ຫຼັງການຈັດຕັ້ງປະຕິບັດ ການຄຸ້ມຄອງ ທີ່ດິນແບບຍືນຍົງ: 0.8
Before conserv.: Ca. 15-30 tCO2eq/ha*a quantify (indicate unit) after conserv.: 0-8 tCO2equ/ha*a specify: mean reduction potential peat bogs: 15tCO2equ/ha*a; fens: 30tCO2equ/ha*a
Perhaps
Re-wetting is only possible on larger scales
